CEE 697z
Organic Compounds in Water and Wastewater
Cyanotoxins Compounds, Toxicity and Occurrence
CEE 697z - Lecture #27
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Lecture #27
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Print version CEE 697z Organic Compounds in Water and Wastewater Cyanotoxins Compounds, Toxicity and Occurrence Lecture #27 CEE 697z - Lecture #27 Cyanotoxins Neurotoxins Anatoxin-a Saxitoxin Anatoxin-as Saxitoxin
Cyanotoxins Compounds, Toxicity and Occurrence
CEE 697z - Lecture #27
Lecture #27
Neurotoxins Anatoxin-a Anatoxin-as Saxitoxin β-Methylamino-L-alanine (BMAA) Hepatotoxins Microsystins Nodularins Cytotoxins Cylindrospermopsin Gastrointestinal and dermatotoxins Aplysiatoxin Lyngbyatoxin a
Anatoxin-a Anatoxin-as Saxitoxin Nodularin R Microcystin LN Cylindrospermopsin Aplysiatoxin BMAA
CEE 697z - Lecture #27
cyanobacterial neurotoxins.
Araoz, R., Molgo, J. and de Marsac, N.T. (2010) Neurotoxic cyanobacterial
828.
CEE 697z - Lecture #27
An Alkaloid Neurotoxin
Residence of these toxins at post-synaptic cholinergic receptors results
in nerve depolarisation
Anatoxin-as is structurally different from Anatoxin–a and is highly
Acetylcholine Anatoxin-a
CEE 697z - Lecture #27
Saxitoxin is usually associated with red tides in marine ecosystems
Responsible for paralytic shelfish poisoning Been detected in some freshwater species
CEE 697z - Lecture #27
analogues produced by some members of different cyanobacteria genera.
Araoz, R., Molgo, J. and de Marsac, N.T. (2010) Neurotoxic cyanobacterial
828.
CEE 697z - Lecture #27
CEE 697z - Lecture #27
CEE 697z - Lecture #27
CEE 697z - Lecture #27
CEE 697z - Lecture #27
Merel, S., Walker, D., Chicana, R., Snyder, S., Baures, E. and Thomas,
knowledge and concerns
blooms and cyanotoxins. Environment International 59, 303- 327.
CEE 697z - Lecture #27
Polypeptide produced by Microsystis & others
Adda is: 3-amino-9-methoxy-2,6,8-trimethyl-10-phenyldeca-4,6-dienoic
acid
90 congeners & 200 related compounds LD50 ~25-60 ug/kg (cyanide is 4,000 ug/kg) Hepatotoxin and tumor promoter
CEE 697z - Lecture #27
Powerful hepatotoxins Cyclic nonribosomal peptide
Similar to microsystins, as both have 3-amino-9-methoxy-2,6,8-trimethyl-10-
phenyldeca-4,6-dienoic acid (Adda)
Difference is Nodularins have 2-(methylamino)-2-dehydrobutyric acid (Mdhb)
where Microsystins have dehydroanaline Produced by Nodularia spumigena, a cyanobacterium
The late summer blooms of Nodularia spumigena are among the largest
cyanobacterial mass occurrences in the world.
More in brackish waters Very similar to microcystins, except that nodularins do not bind covalently to proteins in the body and thus move more easily throughout the body and cells CEE 697z - Lecture #27
microcystins and nodularins.
Merel, S., Walker, D., Chicana, R., Snyder, S., Baures, E. and Thomas, O. (2013) State of knowledge and concerns on cyanobacterial blooms and
International 59, 303-327. CEE 697z - Lecture #27
Alkaloid
CEE 697z - Lecture #27
The molecular structures of cylindrospermopsin (1) and its analogs
7‐deoxy‐cylindrospermopsin (2) and 7‐epicylindrospermopsin (3).
Journal of Applied Microbiology Volume 114, Issue 3, pages 605-620, 19 NOV 2012 DOI: 10.1111/jam.12048 http://onlinelibrary.wiley.com/doi/10.1111/jam.12048/full#jam12048-fig-0001
CEE 697z - Lecture #27
Reference Dose =
amount that can be ingested orally by a person, above which a toxic effect may
milligram per kilogram body weight per day basis.
Dioxin (0.000001 mg/kg-d) Microcystin LR (0.000003 mg/kg-d) Saxitoxin (0.000005 mg/kg-d) PCBs (0.00002 mg/kg-d) Cylindrospermopsin (0.00003 mg/kg-d) Methylmercury (0.0001 mg/kg-d) Anatoxin-A (0.0005 mg/kg-d) DDT (0.0005 mg/kg-d) Selenium (0.005 mg/kg-d) Alachlor (0.01 mg/kg-d) Cyanide (0.02 mg/kg-d) Atrazine (0.04 mg/kg-d) Fluoride (0.06 mg/kg-d) Chlorine (0.1 mg/kg-d) Aluminum (1 mg/kg-d) Ethylene Glycol (2 mg/kg-d) Botulinum toxin A (0.001 mg/kg-d)
T
CEE 697z - Lecture #27
From: Cyanobacteria and Cyanotoxins: Information for Drinking Water Systems , USEPA , Ju
CEE 697z - Lecture #27
blooms and human exposure.
Merel, S., Walker, D., Chicana, R., Snyder, S., Baures, E. and Thomas, O. (2013) State of knowledge and concerns on cyanobacterial blooms and cyanotoxins. Environment International 59, 303-327.
CEE 697z - Lecture #27
Funari E, Testai E. Toxigenic cyanobacteria from marine, brackish and freshwaters. Chart. Critical Reviews in Toxicology, Feb2008; 38(2):98 Available from: Academic Search Premier, Ipswich, MA. Accessed March 20, 2010.
CEE 697z - Lecture #27
Funari E, Testai E. Toxigenic cyanobacteria from marine, brackish and freshwaters. Chart. Critical Reviews in Toxicology, Feb2008; 38(2): 101 Available from: Academic Search Premier, Ipswich, MA. Accessed March 20, 2010.
CEE 697z - Lecture #27
http://healthvermont.gov/enviro/bg_algae/bgalgae.aspx
CEE 697z - Lecture #27
The 2014 T
On-line reports
http://www.nytimes.com/20
14/08/05/us/lifting-ban- toledo-says-its-water-is- safe-to-drink- again.html?_r=0
http://www.vox.com/2014/
8/3/5963645/a-toxic-algae- bloom-has-left-400000- people-in-ohio-without- drinking
CEE 697z - Lecture #27
CEE 697z - Lecture #27
1 ppb WHO drinking water limit 20 ppb WHO swimming limit 60 ppb highest level for Lake Erie till 2011 84 ppb highest level for Grand Lake St. Marys
2000+ Grand Lake St. Marys 2010 1200 Lake Erie Maumee Bay area 2011 Carroll Water System, west of Davis-Besse,
CEE 697z - Lecture #27
Sampling locations and microcystin-LR concentrations (average ± S.E., µg/L) along the Lake Ontario shoreline and the associated rivers, embayments and ponds. The green vertical bar at each Lake Ontario site represents the “shoreside” sampling site. The red vertical bar at each Lake Ontario site represents samples taken in the creek, river or embayment. Vertical bars are to scale. Bars for Knauf and Georgetown Ponds, Lake Neatahwanta, Sackets Harbor “scum” and the Conesus and Silver Lake “scum” concentrations are not to scale with concentration listed above the bar. The vertical bars for the nearshore and offshore of Lake Ontario are labeled “30 m” and “100 m”
CEE 697z - Lecture #27
Average monthly (±S.E.) microcystin-LR, total phosphorus and phycocyanin concentration (µg/L) at 37 sites in Lake Ontario from 2003–2006. Sites include streams, rivers, embayments, shoreside sites, and the nearshore and offshore zones. See Fig. 1 for location of sites.
CEE 697z - Lecture #27
CEE 697z - Lecture #27
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